[go: up one dir, main page]

US3985551A - Process for removing carbon from uranium - Google Patents

Process for removing carbon from uranium Download PDF

Info

Publication number
US3985551A
US3985551A US05/660,907 US66090776A US3985551A US 3985551 A US3985551 A US 3985551A US 66090776 A US66090776 A US 66090776A US 3985551 A US3985551 A US 3985551A
Authority
US
United States
Prior art keywords
uranium
yttrium
carbon
molten
reduced
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired - Lifetime
Application number
US05/660,907
Inventor
George L. Powell
Cressie E. Holcombe, Jr.
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Energy Research and Development Administration ERDA
Original Assignee
Energy Research and Development Administration ERDA
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Energy Research and Development Administration ERDA filed Critical Energy Research and Development Administration ERDA
Priority to US05/660,907 priority Critical patent/US3985551A/en
Application granted granted Critical
Publication of US3985551A publication Critical patent/US3985551A/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B60/00Obtaining metals of atomic number 87 or higher, i.e. radioactive metals
    • C22B60/02Obtaining thorium, uranium, or other actinides
    • C22B60/0204Obtaining thorium, uranium, or other actinides obtaining uranium
    • C22B60/0286Obtaining thorium, uranium, or other actinides obtaining uranium refining, melting, remelting, working up uranium

Definitions

  • This invention was made in the course of, or under a contract with the Energy Research and Development Administration. In its broadest form it relates to the removal of carbon contamination from uranium and uranium alloys by reaction with yttrium.
  • uranium High purity uranium is required for many applications in the nuclear industry.
  • uranium normally picks up carbon from contact with graphite ware and from CO 2 and CO evolved from carbonaceous materials at high temperatures.
  • Carbon contamination is present in molten uranium chiefly as dissolved carbon and in solid uranium as both dissolved carbon and uranium carbide inclusions. This carbon contamination causes considerable reduction in tensile strength, ductility, and corrosion resistance of uranium.
  • the term "carbon contamination” refers to total carbon content, regardless of form. Carbon contamination is particularly bothersome in the production of uranium alloys with alloying metals such as niobium, tantalum, vanadium, and titanium.
  • Such alloys are produced by melting the desired amount of alloying metal with the required amount of uranium or uranium alloy. When the metals are melted together, carbon present in the uranium or uranium alloy feed reacts with the alloying metals forming carbides which float to the top of the melt. This carbide formation makes precise control of the alloy composition very difficult; therefore, the lower the level of carbon contamination in the feed materials, the greater is the composition control capability.
  • insoluble carbides may be concentrated in the top of a melt by sonic vibrations, and soluble carbon contamination may be slightly decreased by vacuum melting uranium in a crucible with a tantalum lid. It was not certain however, whether the tantalum actually reduced the carbon level, and, in any case, the carbon contamination level was reduced only about 15% from 16.5 to 14 ppm.
  • Yttrium has been used as a containment material for molten uranium alloys, (Wilkinson, p. 618), however it was not used as a getter for carbon and its ability as a getter was not recognized.
  • a more expensive and time consuming purification method taught by Wilkinson (238-239) is zone melting, in which a singleturn induction heater is passed slowly over a long solid charge of contaminated uranium to cause localized melting and the concentration of impurities, including carbon, in the ends of the charge which are then cut away.
  • Another method taught by Wilkinson (pp. 238-239) is purification by diffusion, which involves heating uranium in liquid sodium or lithium in a gettering container such as tantalum or thorium. It is taught that this method should be effective for removing oxygen (and possibly carbon and nitrogen), however it is pointed out that the slow rate of diffusion makes this method impractical for any but finely divided uranium. An inexpensive, effective method for removing carbon contamination from both solid and liquid uranium has long been needed.
  • a method for decreasing the level of carbon contamination in uranium comprising confining said uranium in inert atmosphere in effective contact with yttrium, heating the confined metals to 700° -1900° C for causing carbon from said uranium to react with said yttrium forming a yttrium carbide and recovering uranium reduced in carbon content.
  • the reaction is impractically slow and above 1900° C, yttrium carbides melt and decompose to yttrium (which readily volatilizes) and a liquid phase rich in carbon which might re-contaminate the uranium.
  • the contact required in our method is contact effective for causing carbon in the uranium to diffuse to directly contact yttrium and form yttrium carbide.
  • This effective contact is achieved directly by contacting yttrium with molten uranium or indirectly by contacting yttrium with a liquid metal diffusion medium which in turn is in direct contact with uranium (either solid or molten).
  • This invention is a method for decreasing the level of carbon contamination in uranium by using yttrium as a carbon gettering material. While the general method is illustrated with respect to contaminated uranium, it is operable under appropriate conditions for removing carbon from a number of uranium alloys such as U-.75Ti, U-10Mo, U-6Nb, U-7.5Nb-2.5Zr, etc.
  • thermodynamic data for the formation of YC 2 indicate that yttrium would not getter carbon from uranium by formation of this compound.
  • G. V. Samsonov "High Temperature Compounds of Rare Earth Metals With Nonmetals", Consultants Bureau, New York, 1965, states the YC 2 is the most chemically stable compound in the yttrium-carbon system.
  • Effective contact may be accomplished directly by contacting a uranium melt with yttrium in any convenient manner, such as by melting the uranium in a yttrium crucible or by adding slugs or turnings of yttrium to the melt.
  • yttrium reacts with the carbon
  • yttrium carbide is formed which floats to the top of the melt where it is easily separable from the uranium (now reduced in carbon contamination level).
  • the yttrium carbide may be skimmed from the top of the melt, the molten uranium may be drained from the bottom of a bottom-pour crucible, or the melt can be allowed to harden and the top layer (which contains the yttrium carbide) may be sawed off.
  • Effective contact is also achievable indirectly such as by contacting uranium (which in this case may be solid or liquid) with a liquid metal intermediate diffusion medium such as a molten alkali metal which is in direct contact with yttrium.
  • uranium which in this case may be solid or liquid
  • a liquid metal intermediate diffusion medium such as a molten alkali metal which is in direct contact with yttrium.
  • Carbon contamination in the uranium migrates through the diffusion medium and is deposited directly on the surface of the yttrium by the formation of yttrium carbide.
  • Other non-contaminating, low-melting metals may be used as intermediate diffusion media at temperatures above their melting points
  • yttrium contamination may be tolerated within limits in many applications, other uses such as in reactor technology require uranium of higher purity.
  • a particular advantage to the use of yttrium as a carbon getter is that excess yttrium which diffuses into the uranium is easily removable by various methods such as distillation and oxidation to Y 2 O 3 .
  • yttrium contamination may be removed by melting the uranium and contacting it with UO 2 . This causes yttrium to be oxidized to Y 2 O 3 , reducing UO 2 to elemental uranium.
  • This reaction is carried out conveniently by passing molten uranium (contaminated with yttrium) through a bed of UO 2 particles in inert atmosphere at a temperature of about 1200° to 1900° C leaving substantially yttriumfree uranium (less than about 10-100 wt. ppm).
  • a more convenient way of oxidizing excess yttrium, but which results in a small uranium loss, is to contact molten uranium with oxygen which causes the formation of uranium oxides and Y 2 O 3 which float to the top of the melt. This step is conveniently carried out immediately after direct yttrium contact with the melt has resulted in the concentration of yttrium carbide at the top of the melt. Then all the carbide and oxides are removable together leaving uranium reduced in carbon content and relatively yttrium-free.
  • An alternate method of removing yttrium from uranium is to heat the uranium to about 1200° -1400° C which causes a yttrium background vapor pressure of greater than or equal to 10 - 5 torr.
  • yttrium present in the uranium is vaporized leaving substantially yttrium-free uranium behind (less than about 10 wt. ppm). This vaporization is significantly accelerated if the yttrium vapor is pumped away, or is collected on a sorbitive surface such as carbon (which should be previously heated in a vacuum to remove residual CO and CO 2 which might contaminate the uranium).
  • the tests were conducted as follows: A 3 mm. cube of reactor grade uranium contaminated with carbon was placed in a niobium-1 wt.% zirconium crucible having an interior diameter of about 20 mm. The crucible was heated to 200° C and molten lithium was added to cover the uranium cube to a depth of about 5 mm. The crucible was then covered with a niobium-1 wt.% zirconium fitted on the inner side with a rod of gettering material (either yttrium, zirconium, or titanium) such that the gettering material contacted the molten lithium but not the uranium cube.
  • gettering material either yttrium, zirconium, or titanium
  • the surface area of the gettering material contacting the lithium was the same in all cases, 100 sq. mm.
  • the gettering material and the uranium were separated by about 3 mm. of lithium.
  • the covered crucible was cooled and transferred to the evacuated chamber of an electron beam welder.
  • the chamber and covered crucible were further evacuated to 1 ⁇ 10 - 3 MPa pressure and the lid was sealed to the crucible with an electron beam weld.
  • the sealed capsule was heated to the specified temperature for the specified time. After the capsule was cooled to room temperature, the lid was removed and the uranium was recovered and analyzed with a carbon analyzer and optical metallography.
  • This mode is preferred for temperatures below 1132° C where the uranium is not melted.
  • a covered bottom-pour tungsten or niobium crucible lined with a CaO or MgO ceramic liner 1000 kg. of uranium turnings or scrap containing 400-800 wt. ppm of carbon are heated with a metallic diffusion medium of alkali or alkaline earth metal, preferably sodium, lithium or calcium, to 1100° C in inert atmosphere or vacuum and held for 2 hours to allow carbon to diffuse to the yttrium rod.
  • the diffusion medium is molten and lies above the denser uranium, which melts at about 1132° C.
  • the heating rate is not critical.
  • the crucible cover is equipped with a yttrium getter rod or plate which extends downwardly into the crucible, contacting the diffusion medium without directly contacting the uranium metal.
  • the getter rod may be pure yttrium or a non-contaminating alloy such as Y-Mg.
  • the amount of yttrium immersed in the molten diffusion medium should be about 1-4 kg.
  • the temperature is raised to 1200° C to melt the uranium.
  • the bottom-pour crucible should be equipped with a valve means such as a ceramic draw plate, to allow the uranium to be drained from the crucible leaving the diffusion medium behind.
  • the uranium is selectively drained as much as possible.
  • the crucible is cooled under an inert gas purge and is ready for another run.
  • the getter rod is inspected for excess carbon content and replaced if necessary.
  • the diffusion medium is reusable in subsequent runs. If necessary, any residual diffusion medium remaining with the uranium may be boiled away by melting the uranium at 1200° C in a vacuum of about 10 - 2 torr to cause the diffusion medium to evaporate.
  • Examples II, III, and IV demonstrate direct contact between the uranium and the yttrium followed by subsequent yttrium removal.
  • yttrium Four kg. of yttrium is heated with 2000 kg. of carboncontaminated uranium (800 wt. ppm carbon) in a vacuum (about 10 - 4 torr or less) or inert atmosphere in a carbon-free furnace for example, a conventional-type vacuum induction furnace with carbon susceptors.
  • the metals are heated in a carbon-free ceramic or ceramic coated crucible such as MgO, CaO, Y 2 O 3 , ZrO 2 , etc. to 1200° -1400° C at a rate of 300° -500° C/hr. and held for at least about 30 minutes to 2 hours, and cooled.
  • the heating and cooling rates are not critical.
  • the molar amount of yttrium must exceed the molar amount of carbon in the uranium and should be at least 0.2 wt.% of the total charge.
  • yttrium may be removed from the recovered uranium by melting the ingot and passing the molten metal through a bed of uranium oxide to oxidize the yttrium to Y 2 O 3 and reduce the uranium oxide to uranium.
  • a uranium ingot containing 1000-1800 wt. ppm yttrium is placed in a carbon-free, bottom-pour ceramic crucible atop a bed of uranium oxide, such as U 3 O 8 , etc.
  • the crucible is heated to above the melting point of the ingot, about 1132° C, and the molten metal drains through the bed, slowly exiting the bottom of the crucible through a drip plug, such as porous ceramic plug of material wet by uranium such as NbC. Y 2 O 3 remains in the bed.
  • the uranium drips into a ceramic catch mold; for example, MgO.
  • the uranium oxide bed is usable for subsequent runs until more than about 50% of the oxide has been reduced.
  • the yttrium level in the uranium is now reduced to 10-100 wt. ppm.
  • An alternative method for removing yttrium from the carbonfree uranium produced in Example II is by distillation in vacuum or inert gas.
  • a 1000 kg. uranium ingot containing 1000-1800 wt. ppm yttrium is heated in an inert atmosphere (preferably a vacuum of at least 10 - 4 torr) to 1200° -1400° C in an open ceramic crucible such as MgO.
  • a carbon plate (previously outgassed at 1900° C for 60 minutes in a vacuum of 10 - 7 torr) is mounted above the crucible supported by refractory metal braces (such as tungsten).
  • the carbon may be any conventional form, preferably activated carbon.
  • yttrium in the uranium ingot evaporates and reacts with the carbon surface forming a yttrium carbide.
  • the carbon plate acts as a yttrium sink or pump to cause the further evaporation of yttrium.
  • the vapor pressure of yttrium is about 10 - 5 torr and the vapor pressure of uranium is about 10 - 7 torr.
  • uranium has a vapor pressure greater than 10 - 5 torr and significant amounts would be vaporized.
  • the uranium should be heated for sufficient time to remove most of the yttrium. After about 2 hours, the yttrium content within the uranium is reduced to 10-50 wt. ppm.
  • This example demonstrates the removal of yttrium from a uranium ingot by oxidation with gaseous oxygen.
  • Yttrium and uranium are melted together as in Example II in inert atmosphere to cause yttrium carbide to float to the top of the melt.
  • a lance (tungsten for example) is inserted into the melt and an argon-oxygen blend is passed through the melt for about 5 minutes.
  • the oxygen content of the mixture is not critical and the preferred range is 5 to 25 vol. % oxygen.
  • the lance is withdrawn and the melt remains molten for an additional 20 minutes to allow Y 2 O 3 and uranium oxides to float to the top.
  • the metal is then cast into a suitable mold and the top surface, which contains the yttrium carbide and oxides is sawed off.
  • the remaining uranium has 10-50 wt. ppm yttrium.

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • General Life Sciences & Earth Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Chemical & Material Sciences (AREA)
  • Environmental & Geological Engineering (AREA)
  • Geology (AREA)
  • Manufacturing & Machinery (AREA)
  • Materials Engineering (AREA)
  • Mechanical Engineering (AREA)
  • Metallurgy (AREA)
  • Organic Chemistry (AREA)
  • Manufacture And Refinement Of Metals (AREA)

Abstract

Carbon contamination is removed from uranium and uranium alloys by heating in inert atmosphere to 700 DEG -1900 DEG C in effective contact with yttrium to cause carbon in the uranium to react with the yttrium. The yttrium is either in direct contact with the contaminated uranium or in indirect contact by means of an intermediate transport medium.

Description

BACKGROUND OF THE INVENTION
This invention was made in the course of, or under a contract with the Energy Research and Development Administration. In its broadest form it relates to the removal of carbon contamination from uranium and uranium alloys by reaction with yttrium.
High purity uranium is required for many applications in the nuclear industry. During the course of refining and melting operations, uranium normally picks up carbon from contact with graphite ware and from CO2 and CO evolved from carbonaceous materials at high temperatures. Carbon contamination is present in molten uranium chiefly as dissolved carbon and in solid uranium as both dissolved carbon and uranium carbide inclusions. This carbon contamination causes considerable reduction in tensile strength, ductility, and corrosion resistance of uranium. For purposes of this invention, the term "carbon contamination" refers to total carbon content, regardless of form. Carbon contamination is particularly bothersome in the production of uranium alloys with alloying metals such as niobium, tantalum, vanadium, and titanium. Such alloys are produced by melting the desired amount of alloying metal with the required amount of uranium or uranium alloy. When the metals are melted together, carbon present in the uranium or uranium alloy feed reacts with the alloying metals forming carbides which float to the top of the melt. This carbide formation makes precise control of the alloy composition very difficult; therefore, the lower the level of carbon contamination in the feed materials, the greater is the composition control capability.
PRIOR ART
The carbon contamination problem in uranium and uranium alloys is well known in the prior art. A variety of methods for dealing with the problem has been proposed, some involving the use of gettering metals selected from groups IVB, VB, and VIB of the periodic table such as titanium, zirconium, tantalum, and molybdenum. Several methods for removing carbon contamination from uranium and uranium alloys are described by Walter D. Wilkinson in Uranium Metallurgy, Vol. 1, available from Interscience Publishers (New York and London) 1962. According to Wilkinson (pp. 213-214) insoluble carbides may be concentrated in the top of a melt by sonic vibrations, and soluble carbon contamination may be slightly decreased by vacuum melting uranium in a crucible with a tantalum lid. It was not certain however, whether the tantalum actually reduced the carbon level, and, in any case, the carbon contamination level was reduced only about 15% from 16.5 to 14 ppm. Yttrium has been used as a containment material for molten uranium alloys, (Wilkinson, p. 618), however it was not used as a getter for carbon and its ability as a getter was not recognized.
A more expensive and time consuming purification method taught by Wilkinson (238-239) is zone melting, in which a singleturn induction heater is passed slowly over a long solid charge of contaminated uranium to cause localized melting and the concentration of impurities, including carbon, in the ends of the charge which are then cut away. Another method taught by Wilkinson (pp. 238-239) is purification by diffusion, which involves heating uranium in liquid sodium or lithium in a gettering container such as tantalum or thorium. It is taught that this method should be effective for removing oxygen (and possibly carbon and nitrogen), however it is pointed out that the slow rate of diffusion makes this method impractical for any but finely divided uranium. An inexpensive, effective method for removing carbon contamination from both solid and liquid uranium has long been needed.
SUMMARY OF THE INVENTION
It is an object of this invention to provide an inexpensive, highly efficient method for removing carbon contamination (both dissolved carbon and uranium carbide inclusions) from uranium and uranium alloys. It is a further object to provide a process which is effective for uranium and uranium alloys in both the solid and liquid states.
These and other objects are accomplished by providing a method for decreasing the level of carbon contamination in uranium comprising confining said uranium in inert atmosphere in effective contact with yttrium, heating the confined metals to 700° -1900° C for causing carbon from said uranium to react with said yttrium forming a yttrium carbide and recovering uranium reduced in carbon content. Below 700° C, the reaction is impractically slow and above 1900° C, yttrium carbides melt and decompose to yttrium (which readily volatilizes) and a liquid phase rich in carbon which might re-contaminate the uranium.
The contact required in our method is contact effective for causing carbon in the uranium to diffuse to directly contact yttrium and form yttrium carbide. This effective contact is achieved directly by contacting yttrium with molten uranium or indirectly by contacting yttrium with a liquid metal diffusion medium which in turn is in direct contact with uranium (either solid or molten).
DETAILED DESCRIPTION
This invention is a method for decreasing the level of carbon contamination in uranium by using yttrium as a carbon gettering material. While the general method is illustrated with respect to contaminated uranium, it is operable under appropriate conditions for removing carbon from a number of uranium alloys such as U-.75Ti, U-10Mo, U-6Nb, U-7.5Nb-2.5Zr, etc.
For a metal to be an effective getter for removing carbon from uranium it is necessary that the metal react with carbon under the process conditions to form a carbide significantly more stable than uranium carbide. Generally, the more thermodynamically stable the metal carbide compound with respect to uranium carbide, the more effective is the metal for removing carbon contamination. Carbon getters are normally thought to be found in groups IVB, VB, and VIB of the periodic table (Webster's Seventh New Collegiate Dictionary, G. and C. Merriam Co., Springfield, Massachusetts), unlike yttrium, found in group IIIB.
The unexpected efficiency of yttrium as a getter for carbon from uranium is not fully explained by published thermodynamic data. In a 1971 report published by the Molybdenum Corporation of America, Iowa State University Report IS-RIC-5: "Thermochemistry of the Rare Earth Carbides, Nitrides, and Sulfides for Steelmaking", thermodynamic data for the formation of YC2 indicate that yttrium would not getter carbon from uranium by formation of this compound. Another reference, G. V. Samsonov, "High Temperature Compounds of Rare Earth Metals With Nonmetals", Consultants Bureau, New York, 1965, states the YC2 is the most chemically stable compound in the yttrium-carbon system. Based upon these references, the gettering of carbon from uranium by yttrium with the formation of a stable yttrium carbide was most surprising. The specific yttrium carbide stoichiometry of the reaction product is not known. It will be termed yttrium carbide for purposes of this disclosure. It is believed that perhaps other gettering materials are diffusion inhibited and yttrium's effectiveness is a combination thermodynamic effect and kinetic effect.
In order to practice our invention in its broadest form, all that is necessary for removing carbon contamination from uranium is that the contaminated uranium be effectively contacted with yttrium in inert atmosphere (vacuum, noble gas or other non-reactive atmosphere) at a temperature of 700° -1900° C. Under these conditions, carbon from the contaminated uranium reacts with the yttrium forming a yttrium carbide. For purposes of this invention, effective contact is contact effective for achieving the reaction of yttrium with carbon contamination from the uranium. Effective contact may be accomplished directly by contacting a uranium melt with yttrium in any convenient manner, such as by melting the uranium in a yttrium crucible or by adding slugs or turnings of yttrium to the melt. When the yttrium reacts with the carbon, yttrium carbide is formed which floats to the top of the melt where it is easily separable from the uranium (now reduced in carbon contamination level). For example, the yttrium carbide may be skimmed from the top of the melt, the molten uranium may be drained from the bottom of a bottom-pour crucible, or the melt can be allowed to harden and the top layer (which contains the yttrium carbide) may be sawed off. Effective contact is also achievable indirectly such as by contacting uranium (which in this case may be solid or liquid) with a liquid metal intermediate diffusion medium such as a molten alkali metal which is in direct contact with yttrium. Carbon contamination in the uranium migrates through the diffusion medium and is deposited directly on the surface of the yttrium by the formation of yttrium carbide. Other non-contaminating, low-melting metals may be used as intermediate diffusion media at temperatures above their melting points; for example, alkaline earth metals such as calcium, barium and strontium.
When the uranium is effectively contacted with yttrium according to this invention, some diffusion of yttrium into uranium is likely to occur, especially where molten uranium is directly contacted with yttrium. While yttrium contamination may be tolerated within limits in many applications, other uses such as in reactor technology require uranium of higher purity.
A particular advantage to the use of yttrium as a carbon getter is that excess yttrium which diffuses into the uranium is easily removable by various methods such as distillation and oxidation to Y2 O3. For example, yttrium contamination may be removed by melting the uranium and contacting it with UO2. This causes yttrium to be oxidized to Y2 O3, reducing UO2 to elemental uranium. This reaction is carried out conveniently by passing molten uranium (contaminated with yttrium) through a bed of UO2 particles in inert atmosphere at a temperature of about 1200° to 1900° C leaving substantially yttriumfree uranium (less than about 10-100 wt. ppm).
A more convenient way of oxidizing excess yttrium, but which results in a small uranium loss, is to contact molten uranium with oxygen which causes the formation of uranium oxides and Y2 O3 which float to the top of the melt. This step is conveniently carried out immediately after direct yttrium contact with the melt has resulted in the concentration of yttrium carbide at the top of the melt. Then all the carbide and oxides are removable together leaving uranium reduced in carbon content and relatively yttrium-free.
An alternate method of removing yttrium from uranium is to heat the uranium to about 1200° -1400° C which causes a yttrium background vapor pressure of greater than or equal to 10- 5 torr. Under vacuum or flowing inert gas, yttrium present in the uranium is vaporized leaving substantially yttrium-free uranium behind (less than about 10 wt. ppm). This vaporization is significantly accelerated if the yttrium vapor is pumped away, or is collected on a sorbitive surface such as carbon (which should be previously heated in a vacuum to remove residual CO and CO2 which might contaminate the uranium). The ease of removing yttrium from uranium makes yttrium very attractive as a carbon getter. In general, metals from groups IVB, VB, and VIB have high solubilities in uranium and very low vapor pressures. These metals form oxides which are either less stable than uranium oxides or only slightly more stable. Hence it would be extremely difficult to remove these metals from uranium by oxidation or distillation. To demonstrate the unexpected effectiveness of yttrium as a carbon getter, the following table is presented summarizing an experimental comparison of yttrium with titanium and zirconium (normally thought to be very effective carbon getters). As indicated in the table, yttrium is a much better carbon getter than titanium and at least as good as zirconium at low temperatures.
                                  TABLE I                                 
__________________________________________________________________________
                      Amount of Carbon in                                 
                                  Amount of Carbon in                     
Gettering                                                                 
      Temperature at                                                      
              Time of Test                                                
                      Uranium Before Test                                 
                                  Uranium After Test                      
                                              Percent Carbon              
Material                                                                  
      Test °C                                                      
              Sec. × 10.sup.3                                       
                      (PPM)       (PPM)       Removed                     
__________________________________________________________________________
Titanium                                                                  
       900    90      796         582         26.8                        
Titanium                                                                  
      1200    10      796         757          4.9                        
Titanium                                                                  
      1200    10      796         532         33.2                        
Titanium                                                                  
      1200    10      796         582         26.8                        
Titanium                                                                  
      1300     7      297         168         43.4                        
Titanium                                                                  
      1300     7      297         190         36.0                        
Zirconium                                                                 
       850    90      633         323         49.0                        
Zirconium                                                                 
       900    90      633         395         37.6                        
Zirconium                                                                 
      1000    180     633         395         37.6                        
Yttrium                                                                   
      1000    90      796         400         49.7                        
Yttrium                                                                   
      1200     4      796          30         96.2                        
Yttrium                                                                   
      1300     7      297          31         89.6                        
__________________________________________________________________________
The tests were conducted as follows: A 3 mm. cube of reactor grade uranium contaminated with carbon was placed in a niobium-1 wt.% zirconium crucible having an interior diameter of about 20 mm. The crucible was heated to 200° C and molten lithium was added to cover the uranium cube to a depth of about 5 mm. The crucible was then covered with a niobium-1 wt.% zirconium fitted on the inner side with a rod of gettering material (either yttrium, zirconium, or titanium) such that the gettering material contacted the molten lithium but not the uranium cube. After assembly, the surface area of the gettering material contacting the lithium was the same in all cases, 100 sq. mm. The gettering material and the uranium were separated by about 3 mm. of lithium. The covered crucible was cooled and transferred to the evacuated chamber of an electron beam welder. The chamber and covered crucible were further evacuated to 1 × 10- 3 MPa pressure and the lid was sealed to the crucible with an electron beam weld. The sealed capsule was heated to the specified temperature for the specified time. After the capsule was cooled to room temperature, the lid was removed and the uranium was recovered and analyzed with a carbon analyzer and optical metallography.
EXAMPLES
The following examples are presented to illustrate preferred operable modes for carrying out the method of this invention. The process conditions are not necessarily optimized. These examples are for purposes of illustration and are not intended to be limiting, the invention being limited only by the claims. While the examples demonstrate the use of yttrium as a carbon getter, scandium and the rare earth metals (particularly monocarbide formers such as cerium and praseodymium) are contemplated as equivalents of yttrium in this method and may be substituted for yttrium with appropriate process modifications.
EXAMPLE I
This mode is preferred for temperatures below 1132° C where the uranium is not melted. In a covered bottom-pour tungsten or niobium crucible lined with a CaO or MgO ceramic liner, 1000 kg. of uranium turnings or scrap containing 400-800 wt. ppm of carbon are heated with a metallic diffusion medium of alkali or alkaline earth metal, preferably sodium, lithium or calcium, to 1100° C in inert atmosphere or vacuum and held for 2 hours to allow carbon to diffuse to the yttrium rod. In this temperature range the diffusion medium is molten and lies above the denser uranium, which melts at about 1132° C. The heating rate is not critical. The crucible cover is equipped with a yttrium getter rod or plate which extends downwardly into the crucible, contacting the diffusion medium without directly contacting the uranium metal. The getter rod may be pure yttrium or a non-contaminating alloy such as Y-Mg. There should be sufficient molten diffusion medium in the crucible to completely contact the uranium as well as the getter rod. The amount of yttrium immersed in the molten diffusion medium should be about 1-4 kg.
In order to selectively remove the uranium from the crucible at the end of the run, the temperature is raised to 1200° C to melt the uranium. The bottom-pour crucible should be equipped with a valve means such as a ceramic draw plate, to allow the uranium to be drained from the crucible leaving the diffusion medium behind. At the end of the run, the uranium is selectively drained as much as possible. The crucible is cooled under an inert gas purge and is ready for another run. The getter rod is inspected for excess carbon content and replaced if necessary. The diffusion medium is reusable in subsequent runs. If necessary, any residual diffusion medium remaining with the uranium may be boiled away by melting the uranium at 1200° C in a vacuum of about 10- 2 torr to cause the diffusion medium to evaporate.
Examples II, III, and IV demonstrate direct contact between the uranium and the yttrium followed by subsequent yttrium removal.
EXAMPLE II
Four kg. of yttrium is heated with 2000 kg. of carboncontaminated uranium (800 wt. ppm carbon) in a vacuum (about 10- 4 torr or less) or inert atmosphere in a carbon-free furnace for example, a conventional-type vacuum induction furnace with carbon susceptors. The metals are heated in a carbon-free ceramic or ceramic coated crucible such as MgO, CaO, Y2 O3, ZrO2, etc. to 1200° -1400° C at a rate of 300° -500° C/hr. and held for at least about 30 minutes to 2 hours, and cooled. The heating and cooling rates are not critical. The molar amount of yttrium must exceed the molar amount of carbon in the uranium and should be at least 0.2 wt.% of the total charge.
During heating, carbon in the uranium reacts with yttrium to form yttrium carbide which floats to the top of the melt (drosses off). Upon cooling, the metal forms into an ingot and the yttrium carbide is concentrated at the top surface. The top surface is sawed off leaving relatively carbon-free uranium, now 10-50 wt. ppm in carbon and 1000-1800 wt. ppm in yttrium.
If desired, yttrium may be removed from the recovered uranium by melting the ingot and passing the molten metal through a bed of uranium oxide to oxidize the yttrium to Y2 O3 and reduce the uranium oxide to uranium. For example, a uranium ingot containing 1000-1800 wt. ppm yttrium is placed in a carbon-free, bottom-pour ceramic crucible atop a bed of uranium oxide, such as U3 O8, etc. The crucible is heated to above the melting point of the ingot, about 1132° C, and the molten metal drains through the bed, slowly exiting the bottom of the crucible through a drip plug, such as porous ceramic plug of material wet by uranium such as NbC. Y2 O3 remains in the bed. The uranium drips into a ceramic catch mold; for example, MgO. The uranium oxide bed is usable for subsequent runs until more than about 50% of the oxide has been reduced. The yttrium level in the uranium is now reduced to 10-100 wt. ppm.
EXAMPLE III
An alternative method for removing yttrium from the carbonfree uranium produced in Example II is by distillation in vacuum or inert gas. A 1000 kg. uranium ingot containing 1000-1800 wt. ppm yttrium is heated in an inert atmosphere (preferably a vacuum of at least 10- 4 torr) to 1200° -1400° C in an open ceramic crucible such as MgO. A carbon plate (previously outgassed at 1900° C for 60 minutes in a vacuum of 10- 7 torr) is mounted above the crucible supported by refractory metal braces (such as tungsten). The carbon may be any conventional form, preferably activated carbon.
Upon heating, yttrium in the uranium ingot evaporates and reacts with the carbon surface forming a yttrium carbide. The carbon plate acts as a yttrium sink or pump to cause the further evaporation of yttrium. In this temperature range the vapor pressure of yttrium is about 10- 5 torr and the vapor pressure of uranium is about 10- 7 torr. Above the 1400° C, uranium has a vapor pressure greater than 10- 5 torr and significant amounts would be vaporized. The uranium should be heated for sufficient time to remove most of the yttrium. After about 2 hours, the yttrium content within the uranium is reduced to 10-50 wt. ppm.
EXAMPLE IV
This example demonstrates the removal of yttrium from a uranium ingot by oxidation with gaseous oxygen. Yttrium and uranium are melted together as in Example II in inert atmosphere to cause yttrium carbide to float to the top of the melt. While the metal is still molten, a lance (tungsten for example) is inserted into the melt and an argon-oxygen blend is passed through the melt for about 5 minutes. The oxygen content of the mixture is not critical and the preferred range is 5 to 25 vol. % oxygen. The lance is withdrawn and the melt remains molten for an additional 20 minutes to allow Y2 O3 and uranium oxides to float to the top. The metal is then cast into a suitable mold and the top surface, which contains the yttrium carbide and oxides is sawed off. The remaining uranium has 10-50 wt. ppm yttrium.

Claims (7)

What is claimed is:
1. A method for decreasing the level of carbon contamination in uranium comprising:
a. confining said uranium in inert atmosphere in effective contact with yttrium
b. heating the confined metals to 700° -1900° C for causing carbon from said uranium to react with said yttrium forming yttrium carbide, and
c. recovering uranium reduced in carbon contamination level.
2. The method of claim 1 wherein said effective contact is provided indirectly by directly contacting said uranium with liquid metal diffusion medium, said diffusion medium being in direct contact with said yttrium.
3. The method of claim 2 wherein said liquid metal diffusion medium is selected from the group of alkali metals and alkaline earth metals.
4. The method of claim 1 wherein said effective contact is provided directly by melting said uranium in direct contact with yttrium whereby yttrium carbide concentrates at the top of the molten uranium, allowing the molten uranium to harden, and thereafter recovering uranium reduced in carbon content.
5. The method of claim 4 further comprising after yttrium carbide concentrates at the top of said molten uranium, contacting the molten uranium with a gaseous stream comprising oxygen for oxidizing excess yttrium to form yttrium oxide which concentrates at the top of said molten uranium.
6. The method of claim 4 further comprising after recovering uranium reduced in carbon content, melting the recovered uranium in contact with uranium oxide for oxidizing excess yttrium to yttrium oxide, and thereafter recovering uranium reduced in yttrium content.
7. The method of claim 4 further comprising after recovering uranium reduced in carbon content, confining the recovered uranium in inert atmosphere in the presence of outgassed carbon, heating the recovered uranium to 1200° -1400° C for causing excess yttrium to evaporate and be sorbed by the carbon, and recovering uranium reduced in yttrium content.
US05/660,907 1976-02-24 1976-02-24 Process for removing carbon from uranium Expired - Lifetime US3985551A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
US05/660,907 US3985551A (en) 1976-02-24 1976-02-24 Process for removing carbon from uranium

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
US05/660,907 US3985551A (en) 1976-02-24 1976-02-24 Process for removing carbon from uranium

Publications (1)

Publication Number Publication Date
US3985551A true US3985551A (en) 1976-10-12

Family

ID=24651436

Family Applications (1)

Application Number Title Priority Date Filing Date
US05/660,907 Expired - Lifetime US3985551A (en) 1976-02-24 1976-02-24 Process for removing carbon from uranium

Country Status (1)

Country Link
US (1) US3985551A (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4252564A (en) * 1979-08-21 1981-02-24 The United States Of America As Represented By The United States Department Of Energy Method for cleaning bomb-reduced uranium derbies
US4701225A (en) * 1985-09-25 1987-10-20 Commissariat A L'energie Atomique Process for the heat treatment of a uranium alloy member
US5025152A (en) * 1988-02-10 1991-06-18 Ultra-Centrifuge Nederland N.V. Apparatus for separating isotopes of uranium
US5238667A (en) * 1989-06-22 1993-08-24 Nuclear Metals, Inc. Method for treating hydrated green salt
CN116411186A (en) * 2021-12-31 2023-07-11 中核北方核燃料元件有限公司 Smelting method for purifying uranium melt by adding rare earth elements

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
NSA vol. 30, Abstract No. 21669 (Avery, J. G.). *
Wilkinson, Uranium Metallurgy vol. No. 1 (1962) Intesciences Publishing Co. pp. 210 -239, 618. *

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4252564A (en) * 1979-08-21 1981-02-24 The United States Of America As Represented By The United States Department Of Energy Method for cleaning bomb-reduced uranium derbies
US4701225A (en) * 1985-09-25 1987-10-20 Commissariat A L'energie Atomique Process for the heat treatment of a uranium alloy member
US5025152A (en) * 1988-02-10 1991-06-18 Ultra-Centrifuge Nederland N.V. Apparatus for separating isotopes of uranium
US5238667A (en) * 1989-06-22 1993-08-24 Nuclear Metals, Inc. Method for treating hydrated green salt
CN116411186A (en) * 2021-12-31 2023-07-11 中核北方核燃料元件有限公司 Smelting method for purifying uranium melt by adding rare earth elements

Similar Documents

Publication Publication Date Title
US3958981A (en) Process for degassing aluminum and aluminum alloys
US5143355A (en) Apparatus for manufacturing oxygen-free copper
EP2455501A1 (en) Method for producing alloy ingots
JPS6137351B2 (en)
US2707679A (en) Methods of producing zirconium and titanium
US2950962A (en) Reduction of fluoride to metal
US4610720A (en) Method for preparing high purity vanadium
US3985551A (en) Process for removing carbon from uranium
US3288593A (en) Purification of metals
CA1036365A (en) Desulfurization of transition metal alloys
JP4856973B2 (en) Manufacturing method of high purity silicon
US4419126A (en) Aluminum purification system
US3492114A (en) Method for alloying highly reactive alloying constituents
US3406056A (en) Methods of and devices for purifying high melting-point metals
US3091525A (en) Deoxidation of refractory metal
US4518421A (en) Process for producing solid metal particles from a bath of metal
US3501291A (en) Method for introducing lithium into high melting alloys and steels
Powell et al. Process for removing carbon from uranium
US3762911A (en) Method of refining scrap especially of copper nickel alloy
US3020151A (en) Beneficiation and recovery of metals
RU2082793C1 (en) Process for preparing hafnium
Ono et al. Deoxidation of high-melting-point metals and alloys in vacuum
US2776886A (en) Process of preparing and treating refractory metals
CS259504B2 (en) Method of inclusions content reduction in steel and equipment for realization of this method
Kamihira et al. Solid state deoxidation of some rare earth metals and reduction of their interstitial impurity concentrations by electron beam melting